Process for purification and recycle of solutions

Abstract: A process for treating a low-concentrated aqueous feed solution comprising at least one aqueous process stream from a pulp mill, which comprises concentrating the feed solution by evaporation to form an evaporation concentrate, and subjecting at least a part of said concentrate to a first electrodialysis treatment, for forming a first electrodialysis concentrate containing salt removed from the evaporation concentrate and at least one diluate depleted in said salt. A plant for carrying out the process according to any of the preceding claims which comprises an evaporator device (1) with an outlet connected to the inlet of an electrodialysis concentrating device (15), and optionally arranged in the liquid flow path therebetween a precipitating device (5) and/or a separating device (9).

Description: This invention relates to a process for treating a low-concentrated aqueous feed solution comprising a salt solution in at least one aqueous process stream from a pulp mill. Said process comprises concentrating the solution by a treatment comprising evaporation, and subjecting at least a part the concentrated feed solution, also denoted evaporation concentrate, to a first electrodialysis treatment, for forming a first electrodialysis concentrate containing salt removed from the evaporation concentrate and at least one diluate depleted of said salt. The feed solution may prior to the evaporation treatment be subjected to a preliminary purification treatment, e.g. filtration, centrifugation, flotation or other mechanical and/or chemical separation treatments, for removing liquid and especially solid impurities. The feed solution may comprise at least one process stream, e.g. effluent, from a chlorine containing bleaching process. The evaporation concentrate produced in the evaporation treatment may have a residual volume of at most 50% of the volume of the feed solution. Preferably the evaporation concentrate is purified by a chemical and/or mechanical treatment prior to the electrodialysis. The invention is thus especially related to a process in which the feed solution comprises one or more aqueous process streams from a pulp mill, such as a wood pulp or other cellulosic pulp mill, and especially pulp bleach process streams, such as bleach effluent streams, formed e.g. in a chlorine containing bleach process or step, such as a chlorine or chlorine oxide bleach process, and containing e.g. chloride and/or chlorate, but optionally also streams formed in an oxygen, ozone or peroxy compound, e.g. hydrogen peroxide, bleach process or step, or other bleach processes or steps, or combinations of any two or more such bleach processes or steps. The process according to this invention may together with or as one or more mechanical and/or chemical purification step(s), especially as a first purification step after the evaporation step, comprise one or more of filtration, centrifugation, ultrafiltration, membrane filtration and flotation, for separating solid and/or liquid dispersed and especially precipitated materials from the solution, which forms a continuous phase. Generally, it is suitable to maintain the solids content in the concentrated solution in the evaporator below about 20 % by weight, such as below 10 % or optionally below 5 %, by weight, e.g. by adding water or diluate recirculated in the process. Solids content is counted as dry solids content with respect to organic and inorganic materials in the evaporator solution. According to another aspect of the invention, a high current efficiency for recovering ions, especially chlorine and/or chlorate ions, especially when present together in the feed solution, e.g. in quantities which are common in chlorine based bleaching process streams, especially effluent streams, can be maintained in the electrodialysis treatment of the concentrated solution. Thus it may be possible and preferable to maintain a total current efficiency of at least 60 % or at least 70 % or optionally at least 80 %, e.g. for the combined removal of anions, such as chlorine and chlorate ions, whereof the current efficiency for the chlorate ion may be e.g. at least 2 %, especially at least 10 % or at least 20 %. Preferably the current density is maintained in the range, and especially in an upper part of the range wherein chlorine as well as chlorate ions show an essentially linear increase of the mass transport through the membranes with increasing current density in the electrodialysis. Thus, the invention relates according to a preferred embodiment to a process for purification and recycling of bleach process streams, especially bleach effluents, e.g. from a closed pulp mill, comprising evaporation of combined or separate bleach process streams, precipitation and separation of organic substances, especially for recycle to a recovery furnace or other suitable furnace for incineration, and desalination by electrodialysis of the resulting aqueous salt solution, normally essentially or entirely of inorganic materials, to form a diluate with reduced salt concentration and a first electrodialysis concentrate of the salts in aqueous solution. The diluate can be at least partly recycled to the evaporator in order to decrease the salt concentration therein and to decrease thereby the temperature needed for performing the evaporation. This may be important especially when the evaporator comprises surfaces of materials of reduced temperature resistance, such as plastics. The evaporation is preferably performed at sub-atmospheric pressure. The diluate may also be recycled to washing steps in the bleaching sequence or to scrubbers or to other places in the pulp mill where water addition is needed. The first electrodialysis concentrate of feed solution comprising a chlorine compound containing bleach effluent often contains mainly chlorate and harmless inorganic salts like sodium chloride and sodium sulphate and may be let out to the sea after a conventional chlorate destruction. It is, however, possible to recover the inorganic salts, especially if they are mainly chloride and chlorate, and purify these further, e.g. for use in a plant for production of sodium chlorate for bleaching. In this case the pulp mill may be closed in a very broad sense. The environmental aspects of pulp and paper manufacture has been in focus for the industry during the past 15 years. Starting with efforts to reduce colour, COD and BOD in bleach effluents and SO 2 in flue gases the emphasis has very much been on reducing chlorinated organics resulting from chlorine based bleaching. Chlorine dioxide bleaching has shown to be an environmentally friendly process. Also totally chlorine chemical free (TCF) bleaching has been developed. In order to reduce all environmental impact of pulp manufacture the industry is now seeking ways to "close" the mill, or in other words eliminate effluents and instead remove a small amount of waste in solid form under controlled conditions. In the totally closed pulp mill this waste will contain only the trace elements once taken up from the ground by the trees and it is the ultimate goal that these can be fed back to the forestal areas. In Tappi J. Febr. (1989) p. 167-170 it is disclosed that lignin can be separated from bleach effluents. Acid and alkaline effluents are mixed with fibres and a cationic polymer. This gave a reduction of 41 to 67 % of the content of chemical oxygen demanding constituents, measured as COD Cr . Other ways to treat bleach plant effluents have also been described, see APPITA '91/187-191. A process is described where the effluent volume is reduced by evaporation in a low temperature evaporator and the produced condensate is recycled back to the pulping process. The remaining concentrate can be further evaporated and burnt to obtain an inorganic salt for landfilling. The evaporation of solutions with high salt concentrations is known to be difficult due to problems with incrustation and increasing boiling temperature. To obtain a total incineration of the bleach plant effluent, it is therefore necessary to combine the first evaporator with expensive and energy consuming high effect evaporators. The process need a separate furnace that can manage combustion of organics in presence of large amounts of chloride. The US patent 3,986,951 assigned to Champion Int Corp discloses an effluent treatment process for a chlorine based bleachery including organics and solids removal before electrodialysis and brine electrolysis. The effluent from the chlorine stage is treated by adding Al 3+ to precipitate organics and suspended solids, filtered and then electrodialyzed to form a diluate stream containing 200 to 600 ppm NaCl which is returned to the bleachery and a concentrated stream containing 5 - 10 wt % NaCl. The latter stream is concentrated further by evaporation to 25 wt % and electrolyzed to form Cl 2 , NaOH and NaOCl. The process is said to permit reusage of water, recovery of chemicals and reduction of sludge if integrated in a pulp mill. This process treats an effluent with low concentration of organics. Thus, it is difficult to obtain an efficient precipitation of organics which increases the risk of negative effects of scaling in the electrodialysis cell. The use of aluminum makes it impossible to recycle the obtained precipitate to the existing furnaces. At the same time the concentration of inorganic salts is very low. The electrodialysis stack must therefore be operated at a low current density and with large effluent volumes which gives large process equipment and high investment cost. The invention is in the following explained with reference to preferred embodiments of the process and with reference to the enclosed drawings. Figure 1 shows an example of a flow sheet for a plant which is suited for carrying out embodiments of the process according to the invention. Figure 2 shows an example of a flow sheet for an electrodialysis device which is suited for use in the process according to this invention. Figure 3 shows an example of a graph of the voltage vs. current density for an embodiment of this invention. Figure 1 shows a flow sketch of a plant comprising as a first concentration device an evaporator 1, with an inlet conduit 2 for a feed solution, a first outlet conduit 3 for separated liquid or vapour, a second outlet conduit 4 for the concentrated liquid connected to a precipitation device 5. Arrows 6,7 indicate inlets for precipitating agents. An outlet conduit 8 from the device 5 is connected to a separating device 9, which may be e.g. a filter, centrifuge, flotation means or any other suitable means for separating the precipitate from the solution. An arrow 10 indicates the removal of the precipitate from the device 9. The separated solution is removed through an outlet conduit 11 connected to a further separating device 12, such as a filter. A conduit 13 for back-washing the device 12 extends to the conduit 8. The precipitation device 5 and separation devices 9 and 12 act as purification devices for purifying the concentrate. An outlet conduit 14 for the separated evaporation concentrate is connected to the inlet of an electrodialysis cell device 15 for feeding said concentrate into said device 15. A first outlet conduit 16 for the depleted concentrate, also denoted diluate, is connected to a tank 17, from which a recirculation conduit 18 extends for recirculation of diluate to the electrodialysis device 15. A second outlet conduit 19 can be used for transferring diluate to an optional second electrodialysis device 20, back to the concentration device 1 through a conduit 21 or to other uses or disposal. The second dialysis concentrate, formed in the device 20, is removed through a conduit 22 and the diluate through a conduit 23 from the second electrodialysis device 20. The first electrodialysis concentrate is removed through a conduit 24 to a tank 25, from which this concentrate can be withdrawn through a conduit 26, e.g. to a not shown device for utilizing the dissolved salt or for disposal. Through a second conduit 27 concentrate can be recirculated to the electrodialysis device 15. The flow sheet indicated in figure 1 is only an example and can be modified in many ways obvious to an expert from the disclosure in this specification and the publications cited herein. As is mentioned above the exemplified embodiment of the invention is related to a process for purification and recycling of bleach effluents from a pulp mill, but the invented processes and devices are generally applicable also for treating other feed solutions, especially solutions with a relatively low concentration of dissolved salt(s), especially inorganic salt(s), and dissolved and/or undissolved organic constituents which should be removed from the feed solution. In a first step, using a preferred embodiment of the invention, the combined or separate bleach effluent(s) is/are subjected to an evaporation treatment, to obtain a concentrated bleach effluent. Before feed to the evaporator the bleach effluent is optionally filtrated to remove particulate matters like for example fibres, precipitated resin, lignin, oxalates or sulphates, and materials in general which may cause problems in the concentration treatment. The filtration can also be installed on a combined feed and recycle flow to the evaporator. The degree of evaporation is preferably at most 50%, preferably at most 25% or at most 15% residual volume, and preferably to at least 1% and usually at least 3% residual volume. The evaporation can be made in any type of evaporator but a low temperature energy efficient evaporator is preferred. The condensate from the evaporator is preferably purified from low molecular weight organic, volatile substances, and can be recycled, e.g. to the washing steps of the bleach plant or other parts of the pulp mill where the quality of the water is acceptable. The pH of the concentrated feed solution, i.e. in this case the concentrated bleach effluent, is suitably adjusted to below about 9 or especially below about 7 or below 4 or 3,5, and preferably to above 0,5 or above 2. The adjustment of pH may be sufficient for causing precipitation of organic materials. The precipitation of organics can also be achieved, or be further enhanced by addition of precipitating chemicals, optionally together with the pH adjustment. Preferably, these chemicals are organic in order to facilitate use or combustion of the precipitate within the pulp mill. Suitably such organic precipitating chemicals are e.g. substances, especially polymers, with high molecular weight, e.g. with a molecular weight of at least 500.000 or at least 1.000.000 and e.g. up to 5.000.000. Examples of such materials are e.g. polyethyleneoxide, cellulose derivatives, such as ethyl-hydroxyethylcellulose, polyacrylamides, polyamine resins, starch derivatives, and similar materials, preferably within the molecular weight ranges stated above, which are efficient agents for flocculation and dewatering. However, it is also possible to add inorganic precipitating chemicals, such as iron chloride, for the precipitation of organic materials. It is preferred to get a precipitate with as high solids content as possible. At the same time the residual organics in the solution phase should be as low as possible to facilitate an efficient and long term stable electrodialysis. At the same time residual water in the precipitate will increase the salt, especially the chloride and chlorate content in the precipitate, which may make it more difficult to incinerate in standard furnaces available at the pulp mill. Due to this reason, it is less suitable to use inorganic precipitation chemicals to improve flocculation and separation. However, it has been found that the removal of organics from the concentrated effluents can be improved by additions of organic polymers,as mentioned above. It has been confirmed that combinations of high molecular polyethylene oxide and/or cellulose derivates, e.g. ethyl hydroxy ethyl cellulose, can be used for this purpose. Other organic polymers, e.g. polyacryl amide, polyamine resin, starch derivates and similar, that are efficient for flocculation and dewatering can also be used in the precipitation and separation steps, but also for further dewatering of the obtained sludge. The acidification can suitably be made with mineral acids and acid salts thereof, e.g. sulphuric, hydrochloric and/or phosphoric acid and/or acid salts of such acids, single or in mixture, or by electrochemical processes. The resulting organic precipitate is separated by centrifuge, filtration, flotation, or other suitable means for solid/liquid separation. Other suitable separation methods, such as membrane filtration or ultra filtration can also be used. The obtained organic precipitate is preferably taken to an existing furnace, preferably a (soda) recovery furnace. Other furnaces could also be used. According to a preferred embodiment it is possible to merely firstly evaporate an acid effluent. Precipitation chemicals, such as sodium hydroxide, sodium carbonate, green liquor or white liquor, may be added in a precipitation stage before or after the evaporation stage but always before the electrodialysis, in order to separate metal ions from the solution through precipitation at an alkaline pH. If the recovery cycle is very sensitive to inorganic salts in the solution, such as chloride feed, the precipitate can be washed with water or acid before being fed to the recovery furnace. Normally the chloride content in the precipitate represents only 0,2 to 2,5 kg/tonne of pulp, which is low enough to enable direct feed to the recovery furnace without washing. The precipitate can also be washed to a remaining inorganics content of preferably at most 3 kg, especially at most 1,5 kg or at most 0,5 kg , e.g. calculated as Cl per tonne of pulp. In case of limiting capacity in the recovery furnace the precipitate can be recycled to other suitable furnaces for incineration. The water solution resulting from the precipitation step can be subject to further purification steps, e. g. filtration, activated carbon or precipitation with inorganic precipitation chemicals, before it is subjected to electrodialysis to form a diluate with reduced salt concentration and a concentrate of the inorganic salts in water solution. Fig.2 shows an example of a flow-chart of an electrodialysis cell. The electrodialysis cell comprises at least one anion selective (A) and one cation selective (K) membrane between an anode and a cathode. Normally the cell comprises multiple pairs of alternating anion selective and cation selective membranes between one anode and one cathode. Pairs of membranes form between them compartments with inlets and outlets for feeding liquids to and withdrawing liquids from said compartments. At the anode, an anode-solution (30) is added and at the cathode, a cathode-solution (31) is added. When the purified bleach effluent (32) is fed into the cell, the anions will migrate through the anion selective membrane towards the anode and the cations will migrate through the cation selective membrane towards the cathode. The water solution will be depleted in salt and is called diluate (D). The concentrate (C) may be prepared in every other compartment. The diluate can be recycled (33) at least partially to the evaporator in order to decrease the salt concentration therein leading to a more energy efficient evaporation and less incrustation and need for cleaning of the evaporator and permitting evaporation with a lower heating medium temperature, and may also be recycled to washing steps in the bleaching sequence or to scrubbers or to other places in the pulp mill where water addition is needed. The diluate can also be subjected to one or more desalination treatments, preferably to one or more electrodialysis treatments for further reduction of the salt content therein. It is preferred to operate the electrodialysis stacks at a high current density to minimize the size and the investment cost. Preferably the current density is from about 10 and suitably up to 10000 A/m 2 , preferably from about 300 A/m 2 and more preferably from about 500 and suitably up to 3000 or up to 1500 A/m 2 . However, the optimal current density depends to a large extent on the amount of chemicals added, e.g. in the bleachery when treating bleach process streams, the degree of evaporation, and on the amount of soluble salts or acids added in the precipitation step(s). Electrodialysis can be performed in electrodialysis stacks operating in parallel and/or in series, and with liquid stream flow in parallel and/or in series. The obtained diluate can be further desalinated in additional electrodialysis stacks operating at lower current densities to obtain a higher degree of desalination before recycle to the evaporator. The part of the diluate that is not recycled to the evaporator can be desalinated in a separate electrodialysis stack to obtain an almost salt free diluate which can be recycled to a pulping process with no risk of getting problems with chlorides in the recovery system. The concentrate (C) is suitably formed in every second chamber of the electrodialysis cell and to the chambers are added concentrated solution (34). The compartments may contain only chlorate (in case of chlorine dioxide bleaching) and harmless inorganic salts in concentrations between 20 and 250 grams per litre and may be let out, e.g. to the sea after a conventional chlorate destruction such as with SO 2 , sulphite or anaerobic biological treatment. From the compartments concentrated solution (35) is withdrawn. It is, however, possible to recover the inorganic salts, which may be mainly chloride and chlorate, and purify these further for use e.g. in a plant for production of sodium chlorate for bleaching. In this case the pulp mill may be closed in a very broad sense. In case heavy metals or other metals harmful to the pulping process are present in the bleach effluent, these may be separated in the electrodialysis step and collected in the concentrate stream, where they may be removed by conventional brine purification processes, many of which are well-know e.g. from patents belonging to this applicant and others. By applying the invention it is possible to use only one low effect evaporator for removing most of the water in the treated process streams since the increase in boiling temperature can be avoided by taking out the organics and the soluble salts separately and recycling the obtained purified diluate to the evaporator. The process also makes it possible to withdraw organics with low enough content of chloride and/or other constituents which are polluting or may cause corrosion and other difficulties, thereby facilitating incineration in existing furnaces. The process is preferably operated so that the effluent is evaporated to a residual volume that gives an efficient flocculation and separation of organic matter. The degree of evaporation depends on the amount of residual organics and also on the concentration of dissolved inorganic material. The flocculation and precipitation is preferably controlled by measuring the pH and adding acid materials to keep it constant at an optimal level for that specific effluent. The separation of precipitated and/or flocculated material is controlled so that the solution phase is substantially free from particulate matter. This can be done by e.g. monitoring the turbidity prior to electrodialysis. To perform the electrodialysis in a cost efficient way, it is preferred to have a fairly high salt concentration. This can be controlled by measuring the conductivity in the concentrate from the evaporator or in the solution phase after the separation. Below a number of examples are given mainly for illustrating the invention and not for restricting the scope of protection. Example 1: A combined bleach effluent from the D and E stages of a sulphate softwood pulp mill was evaporated to a residual volume of 5 %, and with a content of organics, measured as COD Cr , of 19,3 g/l. The concentrated effluent was acidified with concentrated sulphuric acid to different pH between 1,0 and 3,0. The formed precipitate was separated off by centrifugation and analyzed with respect to chloride content and weight-% of precipitate in relation to the total sample volume. The solution phase was analyzed for COD Cr . The results are shown in the table below where it has been assumed that the total effluent volume, 40 m 3 per tonne of pulp, is treated according to the invention: Sample No pH Cl to recovery furnace [kg/tonne of pulp] Precipitate [wt-%] COD Cr in solution [g/l] 1 1,0 1,00 9,1 11,1 2 2,0 0,58 7,5 11,9 3 3,0 0,23 4,1 16,5 Example 2 : In another experiment different polymer precipitation chemicals, polyethylene oxide (PEO) and cellulose derivatives (CD), were used in addition to sulphuric acid to improve the flocculation and separation of organics from an effluent evaporated to 10 % residual volume. The clear solutions were analyzed for COD Cr . The results are shown in the table below. Sample No pH PEO [mg/l] CD [mg/l] COD Cr in solution [g/l] 4 3 - - 10,9 5 3 2 2 7,2 6 3 5 10 6,9 Example 3 : A combined total bleach effluent from a sulphate softwood pulp mill was evaporated to 10 % residual volume. The concentrate was acidified to pH 3 and the precipitated organic substances were separated by centrifugation. The resulting water solution contained 69,0 mM chloride and 11,9 mM chlorate. During electrodialysis at 0,3 kA/m 2 the chlorate was completely removed and the chloride concentration in the diluate was 12,5 mM. The total current efficiency was 83,7 % for removal of chloride and chlorate. The removed chlorate and chloride ions were collected in the concentrate stream from the cell. Example 4: A combined total bleach effluent from a sulphate softwood pulp mill was evaporated to about 5 % residual volume. The concentrate was acidified to pH 2 with concentrated sulphuric acid and the flocculated organic substances were separated by centrifugation. The resulting water solution contained 240 mM chloride and 27 mM chlorate. The solution phase was subjected to electrodialysis in a laboratory stack. By measuring the current vs voltage behaviour it was found that the maximum current density was above 2,0 kA/m 2 for that particular effluent concentrate, see the graph in figure 3 of the enclosed drawings, which shows a linear relationship between the voltage (V) per membrane pair (U[V]) vs. current density (S) over the range 0,1 to 1,5 kA/m 2 . The concentrate was then desalinated at a constant current density of 1,0 kA/m 2 . The current efficiency for removal of chloride and chlorate was 92 %.

Claims: A process for treating a low-concentrated aqueous feed solution comprising a salt solution in at least one aqueous process stream from a pulp mill, characterised in that the feed solution is concentrated by evaporation to form an evaporation concentrate, and subjecting at least a part of said concentrate to a first electrodialysis treatment, for forming a first electrodialysis concentrate containing salt removed from the evaporation concentrate and at least one diluate depleted of said salt. A process according to claim 1, characterised in that the feed solution comprises at least one effluent from a chlorine containing bleaching process. A process according to claim 1 or 2, characterised in that the volume of the evaporation concentrate produced in the evaporation treatment amounts to a residual volume of at most 50% of the volume of the feed solution. A process according to any of the preceding claims, characterised in that the evaporation concentrate is purified by a chemical and/or mechanical treatment prior to the electrodialysis. A process according to claim 4, characterised in that the purification of the evaporation concentrate comprises acidifying to a pH below 7. A process according to claim 4 or 5, characterised in that the purification of the evaporation concentrate comprises adding high molecular weight organic precipitating material and/or inorganic precipitating material. A process according to any of the preceding claims, characterised in that metal ions are precipitated at an alkaline pH before or after the evaporation, by adding precipitating chemicals. A process according to any of the preceding claims, characterised in that solid organic materials separated by the purifying treatment of the evaporation concentrate is burnt in an incinerating device. A process according to any of the preceding claims, characterised in that said first electrodialysis is performed in one or more electrodialysis devices connected in series and/or in parallel electrically and/or in liquid flow, said devices comprising at least one anion-selective and one cation-selective membrane, and preferably a number of unit cells formed by a number of anion-selective and cation-selective membranes resp. arranged alternating as a stack between an anode and a cathode, said membranes forming between them compartments with inlets and outlets for feeding the evaporation concentrate salt solution stream into such compartments, and bringing, with the aid of an electric current between the anode and the cathode, ions to migrate from the evaporation concentrate salt solution through the anion-selective and cation-selective membranes resp. to solvent streams passing through adjacent compartments, forming at least one diluate stream of the thus depleted salt solution and at least one first electrodialysis concentrate stream containing the ions migrated from the evaporation concentrate, said diluate optionally at least partially being recirculated to an electrodialysis process and/or to the evaporation step, and said first electrodialysis concentrate optionally partially being recirculated to an electrodialysis device for renewed concentration, the not-recirculated part being recovered for further treatment, use or deposition. A process according to any of the preceding claims, characterised in that the electrodialysis of the evaporation concentrate is performed with a current density of at least 0.01 kA/m 2 . A process according to any of the preceding claims, characterised in that the diluate stream is at least partially recycled to the evaporator for maintaining the solids content in the evaporator below about 20 % by weight. A process according to any of the preceding claims, characterised in that the first electrodialysis concentrate is at least partially subjected to an electrolysis treatment for transforming a chloride salt into e.g. chlorine, sodium hydroxide, hydrochloric acid and/or chlorate and/or other chlorine-containing products. A process according to any of the preceding claims, characterized in that the diluate from the first electrodialysis treatment is subjected to a second electrodialysis treatment, preferably in a second electrodialysis device, for further desalination, especially prior to recycling to uses in a pulping process different from the evaporation concentration. A process according to any of the preceding claims, characterised in that the first electrodialysis treatment is controlled to give first dialysis concentrate containing as main salt constituents a mixture of chloride and chlorate salts, said electrodialysis treatment being performed with a total current efficiency for the removal of chloride and chlorate ions from the input to the output (first electrodialysis concentrate) of at least 60 %,the current efficiency thereof for chlorate ions preferably being at least 10 % or at least 20 %. A plant for carrying out the process according to any of the preceding claims, characterized by comprising an evaporator device (1) with an outlet connected to the inlet of an electrodialysis concentrating device (15), and optionally arranged in the liquid flow path therebetween a precipitating device (5) and/or a separating device (9). A plant according to claim 15, characterized by comprising a recirculating line (21) for recirculating diluate from the electrodialysis device (15) to the concentrating device (1). A plant according to claim 15 or 16, characterized by comprising a second electrodialysis device (20) arranged for further desalination of the diluate from the first electrodialysis device (15).

Inventors: LANDFORS JOHAN, LANDFORS, JOHAN
Applicants: EKA CHEMICALS AB
Application year: 1994
Main classification: D21C11
IPC codes: D21C11, C02F1, B01D61